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1.
受污染地表水的生物毒性效应分析   总被引:1,自引:1,他引:0  
针对以非常规水源补水的受污染地表水的生态安全问题,文章以北京地区受污染河水为试验用水,利用多组生物效应试验(发光菌、大型蚤和仔鱼)进行急性生物毒性检测,并与污水厂二级出水和再生水厂出水水质进行比较.结果表明:受污染地表水在浓缩倍数达50倍时,发光细菌相对抑制率达到50%以上,大型蚤和仔鱼的急性毒性试验死亡率均达到100...  相似文献   
2.
以青鳉鱼和大型溞为代表性水生生物,研究三唑酮对其不同测试终点的慢性毒性效应.结果显示,以生存、生长、繁殖为测试终点,青鳉鱼的NOEC分别为76,60,5μg/L,基于大型溞蜕皮次数、生长和繁殖的NOEC分别为25,100,200μg/L.由此可见,青鳉鱼比大型溞对三唑酮的毒性更敏感.比较不同测试终点,青鳉鱼的繁殖类指标最敏感,其次是生长、生存;相比大型溞的繁殖以及幼溞的生长,其幼溞的蜕皮次数指标更为敏感.因此,低剂量长期暴露下三唑酮会对水生生物的繁殖能力造成一定的损伤,评价其水生态安全应全面考虑不同生物种群的不同测试终点,尤其是鱼类繁殖毒性效应.  相似文献   
3.
为了评估胜利油田石油开采对水体的影响,采集了东营市主要河流的18个点的水样,实验室条件下利用日本青鳉(Oryzias latipes)及鱼卵孵化试验检测水样的急性和慢性毒性效应. 结果显示,18个水样对日本青鳉幼鱼都没有急性毒性;与对照相比,88.9%的水样对青鳉鱼卵孵化有一定的影响,其中72.2%的水样中鱼卵的孵化率差异极显著(P<0.05);数据分析发现,鱼卵的慢性毒性效应与水质检测中的9个单个观测指标没有显著的相关性(P>0.05).利用日本青鳉评价胜利油田水体毒性效应的方法可行,水体对日本青鳉有一定的慢性毒性效应,而水体污染与胜利油田区油井的空间分布没有明显规律性.   相似文献   
4.
探讨了日本青鳉在两种除草剂阿特拉津和百草枯联合暴露下的逐级行为响应,采用水质安全在线生物预警系统(BEWs)记录行为强度数据,分析不同暴露浓度、不同暴露时间日本青鳉的行为响应.10、5、1和0.1TU的暴露浓度下行为反应时间分别为:0.74、7.7、29.4和42.2h,而每个浓度不同配比之间行为反应时间差异明显.结果表明:在两种除草剂的暴露下,日本青鳉的逐级行为响应既受化合物浓度高低的影响,又受暴露时间的影响,而且每个浓度两种药物不同配比暴露下的青鳉鱼的逐级行为响应基本一致,每个浓度不同配比之间行为反应时间差异明显,即两种作用机制不同的除草剂对日本青鳉的行为毒性是协同作用.  相似文献   
5.
Although 1,1-dichloro-2,2-bis(p-chlorophenyl)-ethylene (p,p′-DDE), the major and most persistent metabolite of dichlorodiphenyltrichloroethane (DDT), was continually detected in wild fishes that showed abnormal gonad development such as intersex, little is known about the impact of p,p′-DDE exposure on gonad development in fishes. To survey the effects of p,p′-DDE on gonadal development and gene expressions, male juvenile (20-d post hatch) Japanese medaka (Oryzias latipes) was exposed to 1, 5, 20, and 100 μg/L p,p′-DDE for two months. Increased hepatosomatic index (HSI) and decreased gonadosomatic index (GSI) were found in the p,p′-DDE-treated groups. Intersex was found in 100 μg/L p,p′-DDE exposure group, as well as 100 ng/L 17α-ethynylestradiol (EE2) group. By quantitative real-time RT-PCR, it was found that gene expressions of vitellogenins (VTG-1, VTG-2), choriogenins (CHG-H, CHG-L), and estrogen receptor α (ER-α) in the liver of the fish were significantly up-regulated by p,p′-DDE exposure. VTG-1 and VTG- 2 were recommended as the preferred biomarker for assessing anti-androgenic p,p′-DDE because they were the highest up-regulated among the genes and showed good dose-response relationship. The up-regulated ER-α suggested that a potential synergetic effect would occur when p,p′-DDE coexists with other ER-α-binding endocrine-disrupting chemicals (EDCs).  相似文献   
6.
查金苗  王子健 《环境科学学报》2005,25(12):1682-1686
提出一套利用日本青鳉胚胎-幼鱼阶段生长、形态学改变和雌雄比例变化的指标体系评价排水的毒性和内分泌干扰效应的方法.该方法属于活体动物的短期和部分生命阶段暴露测试,整个实验周期为21 d,测试过程不依赖复杂的仪器设备,操作简单、成本低.通过在北京市污水、工业废水及其经过生物处理后的排水进行测试,表明其能够比较准确判断排水中是否存在急性毒性、致畸和内分泌干扰效应物质.将其应用于评价不同深度处理工艺出水毒性效果,结果表明反渗透工艺能够去除大部分毒性物质.  相似文献   
7.
Zhang G  Chen L  Chen J  Ren Z  Wang Z  Chon TS 《Chemosphere》2012,87(7):734-741
The Stepwise Behavioral Response Model (SBRM), which is a conceptual model, postulated that an organism displays a time-dependent sequence of compensatory Stepwise Behavioral Response (SBR) during exposure to pollutants above their respective thresholds of resistance. In order to prove the model, in this study, the behavioral responses (BRs) of medaka (Oryzias latipes) in the exposure of Arprocarb (A), Carbofuran (C) and Methomyl (M) were analyzed in an online monitoring system (OMS). The Self-Organizing Map (SOM) was utilized for patterning the obtained behavioral data in 0.1 TU (Toxic Unit), 1 TU, 2 TU, 5 TU, 10 TU and 20 TU treatments with control. Some differences among different Carbamate Pesticides (CPs) were observed in different concentrations and the profiles of behavior strength (BS) on SOM were variable depending upon levels of concentration. The time of the first significant decrease of BS (SD-BS) was in inverse ratio to the CP concentrations. Movement behavior showed by medaka mainly included No effect, Stimulation, Acclimation, Adjustment (Readjustment) and Toxic effect, which proved SBRM as a time-dependence model based on the time series BS data. Meanwhile, it was found that SBRM showed evident stress-dependence. Therefore, it was concluded that medaka SBR was both stress-dependent and time-dependent, which supported and developed SBRM, and data mining by SOM could be efficiently used to illustrate the behavioral processes and to monitor toxic chemicals in the environment.  相似文献   
8.
The fertilized eggs of Japanese medaka (Oryzias latipes) were exposed to estrone (E1) at 5–5000 ng L−1 for 15 d, and the hatched fry were exposed continuously to the same concentrations for the additional 15 d. Adverse effects on hatchability, time to hatching, and gross abnormalities occurred at 50 ng L−1 or above. Then the fry were divided into a continual exposure group, and a water recovery group. When the fry were exposed to E1 for another 60 d, there was a decrease in the hepatosomatic index (HSI) of males and the influence disappeared in the water recovery group. The gonadosonatic index (GSI) of females at 500 ng L−1 decreased significantly in another 60 d exposure. While the fry were maintained in dechlorinated tap water for 60 d, a significant decrease in female GSI was observed at 50 ng L−1 or above. An increased GSI was found in males in both continual exposure and water recovery groups at all E1 treatments. Quantitative RT-PCR showed that vitellogenin-I (Vtg-I) gene expressions in the female liver were significantly down-regulated at 50 ng L−1 in the continual exposure group, and at 500 ng L−1 in the water recovery group, while male Vtg-I genes were significantly up-regulated for all E1 treatments. In addition, all E1 treatments caused sex reversal of males. These results suggest that E1 at 5 ng L−1 or above have unrecoverable impacts on the gonadal growth and development of medaka, even if only early life stages were exposed to E1.  相似文献   
9.
10.
Oil gelling agents are widely used in emergency response of marine oil spills. However, the biological toxicity of oil gelling agents is not well understood. This research aimed to evaluate the environmental safety of oil gelling agents used for rapid removal and cleanup of marine oil spills. We used luminescent bacteria (Acinetobacter sp. Tox2 and Acinetobacter sp. RecA) combined with exposure experiment using marine medaka (Oryzias melastigma) juveniles to detect the acute toxicity and genotoxicity of 10 oil gelling agents. As a result, a certain level of acute toxicity was detected from the oil gelling agent FOA and GMN-01 (the toxicity equivalent to 0.067 mg/L and 0.084 mg/L of HgCl2, respectively), and a certain level of genotoxicity was detected from the oil gelling agent NORSOREX (the toxicity equivalent to 0.307 mg/L of MMC) by the luminescent bacteria test. However, no obvious acute toxicity or genotoxicity was detected from the above three oil gelling agents in fish-exposure experiments. Our results suggest that the 10 oil gelling agents have no obvious acute toxicity or genotoxicity to higher organisms (including marine medaka). The luminescent bacteria test is more sensitive in detecting biological toxicity of oil gelling agents. This study provides a reference for environmental safety evaluation of the oil gelling agents used in the cleaning up of the marine oil spills.  相似文献   
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